ENVIRONMENTAL

MONITORING

PLAN

For Applications of MALATHION 

 

BOLL WEEVIL ERADICATION PROGRAM

Texas 

2011 

 

United States 

Department of

Agriculture 

Animal and 

Plant Health 

Inspection 

Service 

Plant Protection 

and Quarantine 

Prepared by the 

Environmental 

Compliance Team

Human Health 

& 

Endangered and 

Threatened Species

 March 2011 
2011 Environmental Monitoring Plan, Southwestern U.S. 1 

Table of Contents 

HUMAN HEALTH ........................................................................................................................ 2

Objectives ................................................................................................................................... 2

Methods....................................................................................................................................... 2

Drinking Water Monitoring .................................................................................................... 2

Sensitive Site Monitoring ........................................................................................................ 3

Sensitive Site Inventory ........................................................................................................... 3

Dye Card Sampling ................................................................................................................. 4

Communication of Negative Information................................................................................ 5

Occupational Health Monitoring ............................................................................................ 5

Monitoring for Incidents or Complaints ................................................................................. 5

Monitoring for Malathion Spills ............................................................................................. 6

Quality Assurance and Quality Control (QA/QC) Monitoring............................................... 6

Additional Monitoring Requirements for the Lower Rio Grande Valley Zone in Texas ........ 7

ENDANGERED, THREATENED and PROTECTED SPECIES ................................................. 7

Objectives ................................................................................................................................... 7

Methods....................................................................................................................................... 7

Inventory of Endangered and Threatened Species ................................................................. 7

Monitoring for Drift ................................................................................................................ 9

Monitoring for Run-off ............................................................................................................ 9

Monitoring Water.................................................................................................................... 9

Monitoring by Observation and Field Notes ........................................................................ 10

GENERAL MONITORING ISSUES ........................................................................................... 10

Discretionary Monitoring .......................................................................................................... 10

Documentation .......................................................................................................................... 10

Shipping of Samples ................................................................................................................. 11

Supplies ..................................................................................................................................... 11

RESPONSIBILITIES ................................................................................................................... 12

2010 Operational Procedures/Mitigation Measures Checklist ................................................... A-1

Operational Procedures and Mitigation Measures ...................................................................... A-3

Protection Measures .................................................................................................................... B-1

The methods and procedures described in the 2011 Environmental Monitoring Plan are designed 

to ensure compliance with the National Environmental Policy Act, the Endangered Species Act, 

Federal Insecticide Fungicide and Rodenticide Act, and APHIS policy. Each program 

organizational unit (e.g. work unit, zone, region, etc.) should fully implement this plan during the 

2011 boll weevil eradication season. 
2011 Environmental Monitoring Plan, Southwestern U.S. 2 

HUMAN HEALTH

OBJECTIVES

Monitoring for potential human exposure is designed to: 

1. demonstrate the effectiveness of Boll Weevil Eradication Program (the Program) operational 

procedures in excluding or minimizing exposure of the public to Program-applied 

malathion; 

2. collect data which can be used to evaluate whether the assumptions used in the Environmental 

Assessments are valid estimates of potential exposure of the public to Program-applied 

malathion by: 

a. monitoring for aerial spray drift to investigate the overall potential for exposure; 

b. testing crops and water bodies that might be used for human consumption to 

investigate the potential for exposure to malathion through ingestion; 

3. ensure that quality assurance and quality control procedures were followed; and, 

4. conduct additional monitoring to investigate any Program-related complaints or reports of 

adverse effects on public health, worker safety, environmental quality, or non-target 

species. 

METHODS

Drinking Water Monitoring 

Monitoring will be conducted during all treatments where surface water bodies used for human 

consumption lie within 500 feet of cotton fields. Make a list of the reservoirs, cisterns, or other 

water bodies used for human consumption that are within 500 feet of a cotton field within your 

program area. Before Program treatments begin, provide the Environmental Compliance Team 

(ECT) with a description of each site and its relation to nearby cotton fields. If there are no such 

sites, inform the ECT in Riverdale, MD. 

Collect two water samples from each water body at least one week before the first Program 

application of malathion to any nearby field (do not combine these into a single sample). These 

are pre-program samples. Collect them whether or not treatments are expected at the nearby 

fields. Refer to Standard Operating Procedure (SOP) EM-03, Collection of Water Samples. If 

you do not have a copy of this or any other SOP mentioned in this monitoring plan, contact 

Robert Baca of the ECT at (301) 734-7592 or 734-8247. 

When a treatment is scheduled for a cotton field within 500 feet of a water body that is used for 

human consumption, collect two pre-treatment water samples from different locations at the 

edge of the water (do not combine these into a single sample) within 24 hours of each application 

to the field. These are a separate set of pre-treatment samples from those described in the 

previous paragraph. Collect two post-treatment samples from different locations 2 to 4 hours 

after each application of malathion (do not combine these into a single sample). Monitor these 

water bodies with pre- and post-treatment samples during every application of malathion within 

500 feet of the water body. Ship the samples as described below. 
2011 Environmental Monitoring Plan, Southwestern U.S. 3 

Sensitive Site Monitoring 

Monitoring will be conducted where sensitive sites are within 500 feet of a Program-treated 

cotton field. Sensitive sites are defined as areas where people congregate such as residences, 

public buildings, hospitals, day care centers, inpatient clinics, nursing homes, parks, churches, 

and schools. For those programs that do not monitor all of the sensitive sites in their jurisdiction, 

monitor a minimum of three sites per work unit/district/program each week that malathion is 

applied to fields. Monitor these sites by using dye cards to measure potential drift. 

Vegetation samples will not be required as a part of routine monitoring, except for the Lower Rio 

Grande Valley zone in Texas. Specific additional operational procedures and mitigation 

measures for the Lower Rio Grande Valley zone are listed on pages A6-7 (and discussed briefly 

below). However, collection of vegetation samples is recommended for other program areas at 

sites where landowners express concern over possible contamination of vegetation. In such 

situations, it is recommended that pre- and post-treatment vegetation samples be collected. For 

details, refer to SOP EM-07, Collection of Vegetation Samples. 

If you will only be monitoring a subset of all sensitive sites, identify the most critical sensitive 

sites for monitoring (for guidance, you may use SOP EM-22, Selection of Sensitive Sites). Give 

priority to sites that are the most sensitive; for example, closest to the fields, near areas occupied 

by children or medically compromised individuals, etc. 

Sensitive Site Inventory 

Each work unit, district, or program will make a list of sensitive sites that are within 500 feet of 

cotton fields. You may list all sensitive sites within 500 feet of cotton or list sites according to 

the following criteria: 

1. All sensitive sites within 100 feet of cotton fields will be listed. 

2. Sensitive sites 100-300 feet from cotton fields that are a priority for the Program will be 

listed. These sites may include locations of previous complaints, chemically sensitive 

individuals, organic farms, etc. 

3. Sensitive sites 300-500 feet from cotton fields that are of particular interest to the 

Program, but not necessarily priorities, will be listed. Exposure at these sites should be 

negligible at best, but the Program may wish to list the sites based on public concerns. 

4. All sensitive sites within 500 feet of cotton fields where children are likely to be found 

will be listed. These sites include schools, daycare, playgrounds, etc. This is to address a 

potential concern of the Environmental Protection Agency with regard to possible 

exposure of children to malathion on outdoor surfaces. 

The sensitive site lists that are reported to the ECT need only list the type of sensitive site and the 

cotton field identification number associated with that site. It is preferred that these lists be 

submitted in an electronic form, but they may also be submitted as a printed hard copy. The 

additional information previously reported (distance and direction to cotton field, etc.) is to be 

maintained in the local Program office (although it can be included in the site lists). Those work 

units that provided exhaustive lists of sensitive sites in a previous year only need to submit 
2011 Environmental Monitoring Plan, Southwestern U.S. 4 

updates to that list for 2011 (though please specify whether your list is a complete one or only an 

update). If there are no additions, deletions, or changes in field numbers, please send a brief 

communication to the ECT noting the lack of changes. Prior to the start of malathion 

applications, provide the list of sensitive sites to the ECT at the following address: 

Dr. Robert Baca, USDA-APHIS-PPQ, 4700 River Road, Unit 150, Room 5A-04b, 

Riverdale, MD 20737 or via email to robert.m.baca@aphis.usda.gov 

Sensitive site lists will not be required in weevil-free areas. Since any potential treatment in 

these areas would be limited, sensitive sites can be easily identified on an ad hoc basis. Should a 

treatment be required in a weevil-free area, all sensitive sites within 500 feet of the cotton 

field(s) to be treated will be identified and a list provided to the ECT. This list need not be 

provided to the ECT prior to treatment, and may simply be submitted as part of monitoring 

documentation at the site. Residents within 500 feet of the cotton field(s) will be notified in 

advance of the treatment, and environmental monitoring with dye cards will be conducted. 

Additional sampling is not required but may be conducted at the discretion of the Program, in 

order to address particular concerns of residents or the Program. 

Dye Card Sampling 

Dye cards are used to monitor potential drift. Before leaving for the field to set-up dye cards, 

hang a clean dye card from the rear-view mirror of the Program vehicle used during sampling 

(SOP EM-10, Preparation of Control Samples and Collection of Pesticide Samples). This is a 

control card and should remain in place throughout the day. Send this dye card to the USDAAPHIS Center for Plant Health Science and Technology (CPHST) Gulfport Laboratory for 

analysis along with an APHIS 2060 Environmental Monitoring Form for the control dye card, 

whether the card is spotted or not. If your program monitors all sensitive sites with dye cards 

throughout the season, send a representative sample of all control dye cards to the lab for 

analysis. However, the control dye card does not need to be submitted for analysis if all of the 

non-control cards for the day are unspotted, but document the control card on the APHIS 2060 

Environmental Monitoring Form, and send it to the ECT to report the unspotted non-control dye 

cards. 

Before treatment begins, place three dye cards between the cotton field and the sensitive site, at 

the edge of the sensitive site (not the edge of the cotton field), and with approximately 30 feet 

between cards (see SOP EM-01, Collection of Dye Card Samples). Draw a diagram (either on 

the APHIS 2060 form or on a separate sheet) of the card positions relative to the field and the 

sensitive site, indicating the distance and direction of the dye cards and sensitive site from the 

cotton field. Each card should be identified and labeled individually on the diagram. The 

location of each dye card should be selected so that surrounding vegetation does not create an 

obstruction that could interfere with the deposition of malathion on the dye cards. It is 

acceptable to place the cards under a tree or other cover if this situation is representative of the 

area between the treatment site and the sensitive site. Two hours after the treatment is 

completed, collect the dye cards. Label each sample according to its location on the diagram. 
2011 Environmental Monitoring Plan, Southwestern U.S. 5 

DO NOT write on the dye card, but rather on the plastic bag in which the dye card was shipped. 

Writing on the dye card will ruin it for analysis. 

Check each dye card for any visible spotting. 

 If none of the dye cards has a visible spot, then record this information on a single 

APHIS 2060 form, filling out all of the other information on the sheet as well. Make a 

note of the total number of dye cards without spots. Send the yellow copy of the form 

and all diagrams, maps, etc. to the ECT. Do not send these cards to the laboratory for 

analysis, but keep them in your files. Occasionally submit for laboratory analysis for 

quality control purposes, a set of unspotted dye cards (including the control dye card) 

used during monitoring within your work unit, district, or program area. 

 If any of the dye cards in a set has visible spotting, then submit all of the cards 

(even those without spots and the control dye card) to the Gulfport Laboratory for 

analysis. Complete a separate APHIS 2060 form for each individual dye card (i.e. four 

forms and four dye cards will be submitted to the Gulfport Laboratory.) Fill out all of 

the information on each APHIS 2060 form, being sure to record if that particular dye 

card was spotted or not. Ship the samples as described below. Submit the yellow copy 

of the APHIS 2060 forms and supporting documents to the ECT. 

Communication of Negative Information 

Any organizational unit identified as being an active eradication program, but that does not have 

treatments requiring monitoring is expected to convey this information to the ECT. If pesticide 

applications are made to cotton fields, but there are no treatments that require monitoring in a 

given week, a letter or email must be sent to the ECT noting that treatments were conducted but 

were beyond the distances from sensitive sites that would have required monitoring. 

Occupational Health Monitoring 

Field personnel who might be exposed to malathion should be monitored for serum acetyl 

cholinesterase (AChE) activity. Monitoring should include pre-Program baseline blood samples 

collected before exposure to malathion, followed by samples collected periodically throughout 

the season. At termination of employment or several weeks after all malathion applications have 

ended, a post-Program blood sample should also be collected. Blood test results should be 

reviewed by a licensed health care professional and appropriate action taken should a significant 

inhibition of serum AChE be detected or if clinical signs and symptoms of pesticide exposure 

appear. At the end of the treatment season, results of the serum AChE monitoring program 

should be sent to the ECT in such a way that the anonymity of the employees is preserved. 

Monitoring for Incidents or Complaints 

Priority sampling will be conducted to investigate incidents of unknown origin involving 

mortality of non-target species (fish, bees, etc.) or other unintended environmental or human 

health impacts possibly associated with Program-applied malathion. Information about priority 

samples can be found in SOP EM-09, Priority (Emergency) Sampling. Collect priority samples 
2011 Environmental Monitoring Plan, Southwestern U.S. 6 

as soon as possible after the complaint, request, or problem is reported. Contact the ECT at 

(301) 734-7592 or 734-8247 to collaborate on a sampling plan, sampling methods, and types of 

samples to collect in order to optimize the investigation. If the incident occurs on a weekend, 

commence your investigation and sampling without delay, and contact the ECT as soon as 

possible on Monday. 

Proper documentation of the incident, investigation, and samples is extremely important. When 

responding to priority incidents, send to the ECT all GPS maps showing the site, location where 

you collected samples, the cotton field, and spray lines of recent malathion applications. Be sure 

to completely fill out all information on the APHIS 2060 forms with each sample. Be sure to 

provide an incident/complaint report to the ECT, along with any other information that you feel 

will be helpful in resolving the incident (i.e. photos, observations at the site, etc.). 

Monitoring for Malathion Spills 

Malathion spills (whether accidental, improper disposal, or aircraft crashes) should be monitored, 

depending on the nature of the incident, contractual arrangements, Program guidelines or local, 

state and federal procedures. Call ECT personnel immediately, so that proper procedures and 

samples may be taken, if necessary. Sampling usually occurs as for priority incidents described 

above, but personnel must be aware that they may be sampling materials contaminated with 

nearly pure malathion, and appropriate safety measures should be taken. 

Samples containing malathion from spills or accidents can contain enough malathion to ruin 

shipping containers and analytical equipment. Contact the Gulfport Laboratory for information 

on shipping these samples. Note on each sample and accompanying APHIS 2060 form that this 

is a "possible spill sample," so that lab personnel may properly process the sample. 

Quality Assurance and Quality Control (QA/QC) Monitoring 

A QA/QC checklist can be found on pages A1-2. The checklist describes all of the QA/QC 

measures to be conducted by each program organizational unit to assure adherence to Program 

operating procedures, protection measures, and mitigations. At the end of the treatment 

season, the checklist must be signed by the State Program Manager, State EMS, or other 

appropriate personnel indicating that all of the QA/QC activities were followed. Record any 

deviations along with an explanation and any corrective actions taken. Attach this information to 

the checklist. After the conclusion of Program operations for the season, promptly submit the 

signed checklist to the ECT. 

To determine purity of malathion, designated APHIS or Program personnel will collect neat 

(undiluted) malathion samples throughout the growing season from the distribution warehouses, 

airfield or other storage areas. Collection of purity samples must be coordinated with 

appropriate APHIS personnel, so as not to duplicate sampling. Program personnel may sample 

neat malathion that they suspect may have a problem, such as contamination, outside of regular 

purity sampling. Further details can be found in SOP EM-10, Preparation of Control Samples 

and Collection of Pesticide Samples. 
2011 Environmental Monitoring Plan, Southwestern U.S. 7 

Additional Monitoring Requirements for the Lower Rio Grande Valley Zone in Texas 

In addition to the operation procedures and mitigation measures listed on pages A3-5 below, the 

Lower Rio Grande Valley zone has additional procedures and protection measures based on the 

2005 Environmental Assessment for the Lower Rio Grande Valley. Pages A6-7 below show 

additional operational procedures and mitigation measures based on the EA, which includes 

monitoring of vegetation. The operational procedures and mitigation measures on pages A6-7 

should be reviewed and implemented by the staff in the zone. 

ENDANGERED, THREATENED AND PROTECTED SPECIES

OBJECTIVES

Monitoring near endangered and threatened (E&T) and protected species habitat is designed to 

provide data which can be used to evaluate the effectiveness of protection measures established 

for E&T species and critical habitat. Each year, zones, districts, or programs must reassess the 

presence of E&T species and their habitats. Should a species be found in the jurisdiction of a 

Program area that is not addressed in this document or the current Biological Assessment, the 

ECT must be contacted immediately at (301) 734-7592. Appropriate action will be taken to 

implement the proper protection measures and monitoring to assure that Program operations do 

not disturb the species or critical habitat in question. This monitoring plan lists all protected and 

proposed species known to occur in TX as of the writing of this document and their associated 

protection measures on pages B1-7. If any of the listed species is found near Program cotton, the 

protection measure for that species must be implemented. 

METHODS

Inventory of Endangered and Threatened Species 

A complete inventory of all E&T sites near cotton fields is needed to fully evaluate the 

Program’s ability to protect E&T species. Before the first treatments are made, each zone, 

district, and program staff will contact the local U.S. Fish and Wildlife Service (FWS) office 

concerning listed E&T species and the location of their habitats in all counties that may receive 

treatments during 2011 before the first treatments are made. Note that proposed species are also 

shown on pages B1-7 for information purposes only. No monitoring is required with these 

proposed species, but if they become listed as threatened or endangered, it is likely that 

protection measures will come into effect. If proposed species are in an area under your 

jurisdiction, it is strongly advised that the listed protection measures be implemented. Failure to 

implement these protection measures could possibly harm the species, potentially resulting in 

additional and highly restrictive future protection measures. 

Even if you do not expect to treat any fields this year or are in a weevil-free area, it is 

recommended that you contact FWS for the location of protected species that may be near cotton 

fields. Should any fields require treatments, such treatments cannot begin until protected species 

locations are known. Since it can take some time for FWS to respond with the location of the 

protected species, it is in the Program’s best interest to identify those locations ahead of time 

rather than potentially delay possible but unexpected treatments. 
2011 Environmental Monitoring Plan, Southwestern U.S. 8 

Submit to the ECT a report that documents your program’s annual contact with local FWS 

personnel and the location of E&T species and critical habitats near areas expected to be treated 

by your Program. In your report, include the names and affiliations of those consulted, a list of 

E&T species and critical habitats in Program counties, a list of fields by field number where 

treatments would require protection measures for E&T species, and any other details regarding 

specific protection measures to be implemented. Use page B-8 (the “Endangered and Threatened 

Species Site Reporting Form”) to document the presence and location of each E&T species. Use 

additional paper if needed. 

Your list should include any proposed species found near cotton and whether or not the 

protection measures for them will be implemented. If protected species exist beyond distances 

from cotton fields required to implement the protection measures, those species should also be 

listed on the form with a note in the comments section stating that the species are beyond the 

given limits requiring protection measures. Return the completed form to the ECT before 

treatments begin for the year. Send the completed form to: 

Dr. Robert Baca, USDA-APHIS-PPQ, 4700 River Road, Unit 150, Room 5A-04b, 

Riverdale, MD 20737 or via email to robert.m.baca@aphis.usda.gov 

Listed protection measures include buffer zones, observational monitoring, dye card monitoring, 

water monitoring, and run-off monitoring. If a protected species is located near cotton, the listed 

protection measures must be fully implemented. Note that many species are excluded from 

monitoring since it was determined that the Program will have no effect on the species. These 

species are listed on pages B1-9 with an “NE” (for “no effect”) under the protection measures. 

Several protection measures do not require sampling. For example, the measures for the Ozark 

big-eared bat state, “No aerial use within 1⁄4 mile, no ground use within 300 feet of identified 

habitat.” There are no sampling requirements for this species, but the buffer zones must be 

implemented and documented in writing on the “Endangered and Threatened Species Site 

Reporting Form.” 

When monitoring is required, the type of monitoring is specified in the protection measures. 

Descriptions of the types of monitoring are found below. The distance from a cotton field to a 

protected habitat that triggers required monitoring is listed in the protection measures. For 

example, if a protection measure states, “No use within 60 feet of identified aquatic habitat. 

Monitor for run-off,” then run-off monitoring would be required for any cotton field within 60 

feet of the habitat. In this example, if any portion of a cotton field extended into the 60-foot notreatment buffer area, monitoring would be required even though no malathion would be applied 

within the buffer area. 

Protected Species 

In 2007, the bald eagle was removed from protection under the Endangered Species Act, but 

remains federally protected under the Bald and Golden Eagle Protection Act. As a result, 

protection measures for the eagle must still be implemented. There should be no aerial 
2011 Environmental Monitoring Plan, Southwestern U.S. 9 

applications within 1,000 feet of eagle nests, no ground applications within 660 feet of nests, and 

no use within 60 feet of large water bodies (25 feet across) within a one mile radius of the nest 

site. 

Monitoring for Drift 

When a protection measure notes to “Monitor for drift”, dye cards are to be used. Dye cards 

should be placed at the edge of the habitat of the species. Do not place the dye cards next to the 

cotton field, but rather adjacent to the protected habitat. Placing dye cards next to the cotton 

field will not show that the species are being protected. Use the methods described in the Human 

Health section above. 

Monitoring for Run-off 

When a protection measure notes to “Monitor for run-off”, Automatic Runoff Sampling 

Equipment (ARSE) is to be used. When a cotton field is close enough to a protected habitat that 

it requires run-off monitoring, chances are that the cotton field will drain into that habitat at some 

location. Find the location where the field drains into the protected habitat. Refer to SOP EM04, Collection of Run-off Water Samples. Place a cluster of six ARSEs in the bottom of the 

runoff channel just beyond the edge of the field. Be sure the ARSEs are not in a turn-row where 

they might be run over. This cluster of six ARSEs will be combined into a single sample for the 

“near field” sample. From the location where the ARSEs were placed at the field edge, follow 

the same runoff channel towards the protected aquatic habitat. At a point in the runoff channel 

close to the water’s edge, place another cluster of six ARSEs. These six ARSEs will be 

combined into a second single sample for the “away from field” sample. The goal of these two 

samples is to show that any malathion that might run off of a field will decrease in concentration 

down the runoff channel before it enters the aquatic habitat. 

Periodically check on all the ARSEs, and replace any that have been damaged, buried, or 

removed. Provide a detailed description of the drainage including slope, soil type, and ground 

cover. Illustrate your description with an annotated map, aerial photograph, or sketch, and 

include photographs if available. Monitor weather and cancel treatments if rain appears 

imminent (within 8 hours). If it rains at one of the fields being monitored within five days after 

it was last treated, then collect the ARSE samples within 12 hours of when the rain begins. Each 

cluster of six ARSE samples is pooled to make one composite sample. So, there will be two 

samples from each site, one at the field edge (“near field”) and one near the receiving water body 

or drainage point (“away from field”). 

Whenever run-off water samples are collected, also collect a sample of the water body receiving 

the runoff. Directions for collecting water samples are detailed in SOP EM-03, Collection of 

Water Samples. This sample is used to show how malathion that might be detected in the 

ARSEs is diluted upon entry into the water body. 

Monitoring Water 

A few species require water sampling as a protection measure, but these species have not been in 

Program treatment areas in the recent past. If one of these species is found near a treatment area 
2011 Environmental Monitoring Plan, Southwestern U.S. 10 

this year, contact the ECT for information on the appropriate method to protect and sample the 

water body in question. Methods vary depending on if the water body is flowing or stationary. 

For reference, SOP EM-03, Collection of Water Samples can be reviewed, but this does not 

currently cover the sampling of flowing water. 

Monitoring by Observation and Field Notes 

Note-taking is required for most monitoring. Most often a sentence regarding general procedure 

is sufficient (for example: “nothing unusual noted during or after treatment”). Note the time of 

treatment, and any wildlife activity in or around the field at E&T species sites. Refer to SOP 

EM-12 Using a Field Log Book. Submit photocopies of field log books, or make notes directly 

into the “remarks” section of the APHIS 2060 form. In the case of monitoring eagle nests, see 

note-taking recommendations in SOP EM-18 Observing Bald Eagles at Nest Sites. Document 

your observations as required by the protection measures, and submit these notes to the ECT. 

GENERAL MONITORING ISSUES

DISCRETIONARY MONITORING

At the discretion of program managers or staff, additional monitoring samples can be collected. 

Although the monitoring outlined in this plan should be adequate to generate the data needed to 

meet the objectives, additional sampling may be necessary around particular sensitive sites. 

Examples might include sites where there have been problems or complaints in previous years, 

sites that are highly visible to the public or are politically sensitive, sites where environmental 

monitoring might help prevent future concerns, and sites of proposed protected species. 

To assure that sampling equipment is not accidentally exposed to malathion, work units or 

program areas may periodically submit an unused dye card, distilled/deionized water in Program 

containers, or gauze wipes of sampling equipment in storage for analysis of malathion. Submit 

an individual APHIS 2060 form with these samples, as you would with any other sample you 

submit for analysis. 

To independently verify the analyses of the Gulfport Laboratory, work units or program areas 

may periodically follow procedures for taking, documenting, and submitting split samples for 

analysis. Split sampling involves taking a single sample and dividing it in half, with each half 

analyzed for malathion by a different laboratory. If you choose to take split samples of any type, 

contact the ECT at (301) 734-7592 to discuss the proper procedures. 

DOCUMENTATION

Draw a clear diagram of the sensitive site and where each sample is collected, either on a 

Geographic Information System (GIS) map, on a separate piece of paper, or on the APHIS 2060 

forms associated with the samples. If you are collecting a series of samples from the same site, 

submit the map and diagram only once, as long as the site and each sample are clearly indicated 

on the map and in the appropriate sections of each APHIS 2060 form. 
2011 Environmental Monitoring Plan, Southwestern U.S. 11 

Complete a separate APHIS 2060 form for each sample collected. Instructions for completing 

the APHIS 2060 forms may be found on the back of each form. For each sample, submit the 

blue copy of the APHIS 2060 form to the Gulfport Laboratory with the sample, the white copy 

of the form to the lab in the sample shipping container but separate from the sample, and the 

yellow copy of the form (and any maps, photos, etc.) to the ECT. For any samples that are not 

sent to the laboratory for analysis (i.e. unspotted dye cards), send the APHIS 2060 form directly 

to the ECT. Keep the pink copy of each form you submit as a record in your local office. 

Properly identify each sample as “routine” or “priority.” An incorrect identification regarding 

the nature of the sample creates confusion for those who must interpret the data, and delays the 

processing of samples that are incorrectly marked. Mark samples as “priority” only for instances 

where a fast turnaround of samples is required. This applies to all complaint investigations, spill 

incidents, potential human health issues, and other samples considered to be of very high 

importance. Otherwise, mark the sample as “routine.” 

SHIPPING OF SAMPLES

Ship all samples, including dye cards, by using some form of overnight delivery. See SOP EM17, Packaging and Shipping of Samples for details. This applies to all samples, whether they are 

priority or routine. Do not ship samples using USPS Priority Mail or standard ground service 

with other carriers. Overnight delivery allows the sample to stay frozen or at least cold. 

Shipping any other way will take several days and can ruin the sample. 

With the exception of neat (pure) chemical, be sure that all samples are frozen, shipped in a 

cooler box (not a regular cardboard box), and kept cold during shipment. To keep samples cold, 

use dry ice, since it does not turn to liquid when warmed and will therefore not ruin any forms or 

samples. However, if water samples are shipped, do not use dry ice, since it will cause the 

sample containers to crack or break. Since dry ice may not be available in all areas, regular ice 

can be used for shipping any samples, but only if the ice is placed in a separate sealed container. 

Either use “blue ice” containers (the reusable plastic containers with the blue liquid/gel inside) or 

contained regular ice (i.e., sealed in zip-loc bags). Unsealed ice will melt and leak during 

shipment, causing unnecessary concern when received at the laboratory. 

SUPPLIES

As in the past, supplies for monitoring are ordered through the APHIS Gulfport Laboratory. A 

checklist for ordering supplies is located on pages C1-2. The lab prefers that supply orders be 

faxed to them using the numbers listed on the checklist rather then leaving a voice message for 

orders. 
2011 Environmental Monitoring Plan, Southwestern U.S. 12 

RESPONSIBILITIES

USDA-APHIS Environmental Compliance Team 

In addition to preparing this Monitoring Plan, ECT personnel in Riverdale, MD, will: 

1. Review and interpret field and pesticide residue data from the sample collectors and the 

laboratory. Contact the sample collector for clarification as soon as possible if any field 

data is incomplete or unclear. Notify the Program Director and Manager immediately if 

any residue data indicates the possibility of excessive exposure to malathion. 

2. Provide training, clarification, and interpretation on how to implement the Monitoring Plan. 

3. Submit a comprehensive interpretive report to the Program Director and the National 

Coordinator, within 60 working days of receiving all of the Program’s field data and all 

residue data. Following review of the information, the ECT will provide a copy of the 

report to the Environmental Protection Agency and U.S. Fish & Wildlife Service. 

USDA-APHIS-CPHST Gulfport Laboratory 

Personnel at the Center for Plant Health Science and Technology (CPHST) Laboratory in 

Gulfport, MS, will: 

1. Prepare and ship sampling containers and other material required for collection, stabilization, 

and shipping of environmental monitoring samples. 

2. Provide training on methods for collecting, handling, preserving, and shipping samples. 

3. Respond to requests for additional information by field personnel when special sampling 

requirements occur. 

4. Analyze monitoring samples according to standard operating procedures for malathion. 

5. Complete analyses and report results on the following schedule: 

a. Within 23 working days after receipt, complete analyses of all routine samples and 

send results to the ECT. 

b. Within 5 working days after receipt, complete analyses of all priority/emergency 

samples and send results to the ECT. 

c. Contact ECT if the projected completion schedules need to be extended due to sample 

load or instrument problems on site. 

6. Forward copies of all environmental monitoring forms and any attached documentation to the 

ECT each week via overnight mail. 

Program/Foundation/Organization Employees, PPQ Field Service Personnel or 

Cooperators, Under the Direction of the Program Director 

Personnel in work unit, district, and program areas will: 

1. Ensure that sufficient resources from the Program are allocated for completing the monitoring 

activities described in the Environmental Monitoring Plan (EMP). 

2. Coordinate with Federal and local wildlife officials to identify E&T species and habitats near 

or within areas that may be affected by Program activities, inform the ECT of these 

species and locations, and implement the required protection measures. 

3. Identify all sensitive sites near cotton fields as described in the EMP. 
2011 Environmental Monitoring Plan, Southwestern U.S. 13 

4. Select sufficient monitoring sites for the collection of samples. Follow instructions in the 

EMP and referenced SOPs to develop a plan for sample collection and documentation, 

including: 

a. Collection of the type and number of samples recommended in the EMP. 

b. Completion of a separate APHIS 2060 form for each sample that is collected. 

c. Providing all the information necessary (as described above) to document the 

samples. Following each treatment, send all supporting documentation, including a 

copy of the appropriate APHIS 2060 forms to the ECT. Send all samples and 

appropriate APHIS 2060 forms to the Gulfport Laboratory. Ship all samples and 

supporting documentation as soon as possible after collection. 

d. Notification of the lab prior to shipping any priority, spill, or unusual (i.e. other than 

water, dye card, soil, or vegetation) samples. 
A-1 

2011 OPERATIONAL PROCEDURES/MITIGATION MEASURES CHECKLIST

(Modify as needed for each work unit, district, or program area) 

______ Retain a copy of all the pesticide certifications for Program personnel who are applying or supervising the 

application of pesticides. Certificates were reviewed twice per year. 

______ Contractors’ pesticide application certificates were available and recorded prior to the initial pesticide 

application. 

______ Copies of all APHIS Form 2060’s submitted to the USDA analytical laboratory were retained at the work 

unit, district, or program area as documentation of the environmental monitoring program. 

______ A printout, or electronic file, of all trapped cotton fields, and the dates traps were checked and fields were 

treated, was retained as documentation for meeting all trapping and treatment criteria. 

______ Operational Procedures and Recommended Mitigation Measures for using malathion, as defined in the 

National Boll Weevil Cooperative Control Program, Environmental Impact Statement, Tables 2-1 and 2-2 

(attached), were reviewed with all appropriate Program personnel and copies were distributed as 

appropriate. (Measures for chemicals not used by the program may be ignored.) 

______ Sensitive areas as defined in Table 2-1 in the Environmental Impact Statement (attached) were identified in 

each field unit. Appropriate Program supervisory personnel are familiar with all sites and have applied 

appropriate protective measures to avoid negative impact. Program personnel have reviewed these areas 

with field unit supervisors each spring prior to pesticide application, assessed the sites for environmental 

monitoring sampling, and provided appropriate seasonal review. 

______ The following was issued to each employee as appropriate and serve as instructions for operational 

procedures: 

 _____ a. Trapper Guide and Trapper Agreement _____ d. Airplane Observer Duties 

 _____ b. Mist-Blower Operational Guide _____ e. Airport Recorder Duties 

 _____ c. Hi-Boy Operational Guide _____ f. BWEP Safety Manual 

 

______ Mist-blower and hi-boy operator training was conducted. Each employee signed a statement that they have 

received appropriate operational and safety training. This statement is retained in their personnel folder. 

______ Each employee involved with pesticide use was tested for blood acetyl cholinesterase levels as necessary. 

Copies of all cholinesterase tests were retained in each employee's folder. 

______ Global positioning systems (GPS) were required on all aerial application aircraft and generated a record of 

pesticide application. Two-way radio contact was maintained to allow communication between pilots and 

ground observers, to enhance safety and the effectiveness of each treatment. 

______ Wind and weather conditions were recorded to document meteorological conditions during treatments. 

______ Airplane check-in procedures certified nozzle type, size and number, spray system pressure, nozzle 

orientation, etc. This check-in list and subsequent seasonal inspections were retained in the work unit, 

district, or program area office for each aircraft used in the Program. 

______ Correct operational and safety procedures for mist-blowers and hi-boys were monitored weekly by Program 

supervisory personnel and documented in the mist-blower log. Program supervisory personnel checked at 

least one mist-blower operator or hi-boy operator each week during the control season. 
A-2 

______ A minimum of one aerial application operation was monitored by Program supervisory personnel each 

week for each contractor. This monitoring procedure was noted on flight records. 

______ Pesticide labels were carried in the vehicle of all persons involved with application, i.e. mist-blower 

operators, hi-boy operators, airplane observers, field supervisors, and Program supervisory personnel. 

______ Dye cards were labeled as to field numbers, date, and time of application. These cards were inspected by 

Program supervisory personnel and retained in the work unit or program area office or sent to the USDA 

laboratory for analysis as described in the Environmental Monitoring Plan. 

______ Initiation of Program operations was preceded by a notification to the following agencies: 

 _____ a. State Department of Agriculture or similar agency; 

 _____ b. State Conservation and National Resources Agency or similar agency; 

 _____ c. State Forestry Commission or similar agency; 

 _____ d. State Department of the Environment or similar agency; and 

 _____ e. Local governmental and county agencies. (Provide listings below.) 

______ Included in the notification letters was a request for assistance in identification of potential sensitive sites 

near cotton fields. 

______ A safety equipment check-off list was signed by each employee involved in pesticide application. This was 

retained in the employee’s personnel folder. 

______ Safety procedures dealing with exposure to pesticides were inserted into the Program safety manual and 

made available to all employees handling pesticides. 

______ Empty pesticide containers were returned to the distributor. 

______ All complaints were documented, thoroughly investigated, and resolved. Those involving alleged pesticide 

misuse were referred to the appropriate state authority. Copies of complaints and actions taken were 

maintained on file. Copies of any state investigative reports were retained in the work unit or program area 

and copies submitted to the USDA-APHIS Environmental Compliance Team. 

______ Local contacts with U.S. Fish and Wildlife Service concerning endangered and threatened species habitat 

and mitigation measures were documented. 

The above procedures and measures were performed in the __________________________________ work unit, 

district, or program area during the 2011 season. Any minor deviations in such were corrected when observed. 

Deviations and/or pesticide incidents and corrective actions taken have been documented and are described as 

follows: 

_____________________________________________________________________________________________ 

_____________________________________________________________________________________________ 

_____________________________________________________________________________________________ 

_____________________________________________________________________________________________ 

_____________________________________________________________________________________________

_____________________________________________________________________________________________ 

_____________________________________________________________________________________________

_____________________________________________________________________________________________ 

_____________________________________________________________________________________________ 

______________________________________ _____________________ 

Signature Date
A-3 

Operational Procedures and Mitigation Measures 

National Boll Weevil Cooperative Control Program 

These operational procedures and mitigation measures have been adopted for, and are an integral part of, the 

cooperative Boll Weevil Eradication Program. They were printed originally in the programmatic Environmental 

Impact Statement, and were revised as necessary in 2005. 

Table 2-1 Operational Procedures

All Methods of Control 

1. All applicable Federal, State, and local environmental laws and regulations will be followed during boll 

weevil control operations. 

2. Sensitive areas (water bodies; parks; and occupied dwellings, such as homes, schools, churches, hospitals, 

and recreation areas) that may be adjacent to cotton fields will be identified. The program will be 

adjusted accordingly to ensure that these areas are not negatively affected. 

3. Environmental monitoring of the program will be in accordance with the current environmental monitoring 

plan. 

4. All cotton fields will be trapped. During the initial diapause year of the program, all fields will be treated 

from “ten percent cracked boll” until there is no hostable material remaining. In subsequent years, only 

hostable fields from which boll weevils have been caught will be treated. 

5. All program personnel involved in chemical applications will be instructed on the safe use of malathion, the 

safe use of equipment, and on operational procedures. Field supervisors will train Field Technicians, 

mist-blower operators and high-clearance sprayer operators on operational procedures, and monitor their 

conduct during working hours. 

Aerial Applications 

1. All materials will be applied in strict accordance with EPA- and State-approved label instructions. 

2. Aircraft, spray equipment, and pilots that do not meet all contract requirements will not be allowed to 

operate. 

3. All USDA, APHIS, Plant Protection and Quarantine employees who plan, supervise, recommend or perform 

pesticide treatments must be certified under the APHIS pesticide certification plan. They are also 

required to meet any additional requirements of the State where they perform duties involving pesticide 

use. All Foundation personnel involved in pesticide application must maintain State pesticide applicator 

certification as required by State law. 

4. Upon notification by program personnel, growers will advise workers of the re-entry period following 

treatment. 

5. Two-way radios or aircraft radio frequencies will be provided to program personnel who direct, coordinate, 

or observe pesticide applications, to facilitate communication with the pilot. 

6. All APHIS field personnel will have baseline cholinesterase tests before the first application and each spring 

and fall thereafter. It is recommended that contract, State, and private personnel also participate in this 

testing program. 

7. Only certified aerial applicators who have been familiarized with local conditions will be used by the 

program. 

8. To minimize drift and volatilization, applications will not be made when any of the following conditions 

exist in the treatment area: wind velocity exceeds 10 miles per hour (or less if required by State law); 

prevailing wind is blowing toward a nearby residence or other sensitive site; rain is falling or is 

imminent; fog is present, or air is turbulent enough to seriously affect the normal spray pattern; or 

temperature inversions exist that could lead to offsite movement of applied material. 
A-4 

9. Nozzle types and sizes, spray system pressure, and nozzle orientation will be specified in the program’s 

aerial application contract or as otherwise directed by program personnel. 

Ground Applications 

1. Mist-Blowers 

 • Operators will be certified applicators, or will be in constant radio or cell phone contact with certified 

applicators. 

 • Units will be operated from closed truck cabs with operators using re-circulated air. 

2. High-Clearance Sprayers 

 • Operators will be certified applicators, or will be in constant radio or cell phone contact with certified 

applicators. 

 • Spray operations will be conducted from closed cabs using re-circulated air. 

Table 2-2. Recommended Mitigation Measures 

All required State and local authorities will be notified upon initiation of the program. The notification will 

advise State and local authorities of the need for any assistance in identifying sensitive areas in proposed 

treatment areas. 

Protection of Workers 

All program personnel will be instructed on emergency procedures to follow in the event of insecticide 

exposure. Equipment necessary for immediate washing procedures must be available for application personnel. 

Aerial Applications 

1. Pilots, loaders, and other personnel handling insecticides will be advised to wear safety equipment and 

protective clothing. 

2. Program personnel observing applications of malathion are required to wear protective clothing or remain 

inside a closed vehicle with re-circulating air, depending on the circumstances of the application. 

3. Application operations will be postponed in fields in which people are working. These fields will not be 

treated when workers are present. 

4. GPS systems are required on all contract aircraft. They will be used for pilot guidance, mapping fields to be 

treated, and assistance in locating fields and marking swaths. 

Ground Applications 

1. Mist-Blowers 

 • Operators will be certified applicators, or will be in constant radio or cell phone contact with certified 

applicators. 

 • Operators will wear appropriate safety equipment when loading or servicing the unit, and will be 

specially trained by program personnel. 

 • Mist-blower units will be operated from closed truck cabs with operators using re-circulated air. 

2. High-Clearance Sprayers 

 • Operators will be certified applicators, or will be in constant radio or cell phone contact with certified 

applicators. 

 • Operators will wear appropriate safety equipment and protective clothing when loading or servicing 

the unit. 

 • High-clearance sprayers will be operated from closed cabs with operators using re-circulated air. 
A-5 

Pesticide Handling Precautions 

1. Insecticides will be delivered and stored in sealed totes (mini-bulk tanks) or drums and then pumped directly 

into the spraying equipment. 

2. All insecticides will be stored in accordance with Federal, State, and local regulations and label instructions. 

3. All loading and unloading of insecticides will be within a containment area where an accidental spill will not 

contaminate a stream or other body of water. 

4. In the event of an accidental spill, procedures set forth in the PPQ Treatment Manual, chapter 7, pages 7-3-1 

through 7-3-18, entitled, “Guidelines for Managing Pesticide Spills” will be followed. 

5. All empty insecticide totes (mini-bulk tanks) and drums will be returned to the distributor for reconditioning. 

Protection of the Public 

1. Application aircraft shall avoid direct spraying of residences, garden plots and adjacent crops at all times. 

2. Program personnel shall immediately cease spraying operations if members of the public are observed within 

100 feet of a cotton field being sprayed with malathion. 

Protection of Bees 

Before beginning treatment with malathion, program personnel shall notify all registered apiarists in or near the 

treatment area of the date and approximate time of chemical treatment. 

Protection of Wildlife 

1. All control operations will be conducted with appropriate concern for their potential impact on endangered, 

threatened, proposed and protected species identified in this document. 

APHIS has prepared a biological assessment for federally listed endangered, threatened, proposed and protected 

species found within all U.S. cotton-producing counties from species information provided by the U.S. 

Department of the Interior, Fish and Wildlife Service (FWS) and State wildlife agencies. 

Adequate protection measures are developed for federally listed endangered, threatened, proposed and protected 

species through the Endangered Species Act, section 7, formal and informal consultations with FWS. 

Specific biological and distributional data for species is gathered in discussions between APHIS, Plant 

Protection and Quarantine, local FWS offices, State wildlife agencies and the Foundation before 

operations begin. 

Species and habitats protected by State laws are addressed in site-specific assessments as needed. 

2. Oil-sensitive dye cards are used to regularly monitor application efficacy. Spray deposition in the target area 

and droplet size are critical concerns. 
A-6 

Additional Operational Procedures and Mitigation Measures 

Lower Rio Grande Valley Boll Weevil Eradication Program 

Environmental Assessment - 2005 

Site-specific Protective Measures Leading to a Finding of No Significant Impact 

The site-specific protective measures described in this subsection were designed specially for the Lower Rio 

Grande Valley Boll Weevil Eradication Program. These are the minimum measures that, in the estimation of the 

program managers, are required to ensure that implementation of the proposed program will result in no 

significant impact. 

Additional Precautions for Treatments 

1. Only malathion (the least toxic of the available organophosphate insecticides) will be used by the Lower Rio 

Grande Valley Boll Weevil Eradication Program. 

2. Aerial applications of pesticides will be made at a height of 5 feet or less above the cotton canopy, unless 

precluded by obstructions. 

3. Program personnel will familiarize aerial applicators with applicable operational procedures, mitigation 

measures, and protection measures that will be required. 

4. Aerial applications of pesticides will not be made to sensitive areas (residences, public buildings, bodies of 

water, hospitals, primary and secondary schools, day care centers, inpatient clinics, nursing homes, 

parks, churches); program pesticides will only be applied to cotton fields. 

5. Program personnel will be present during all treatments near colonias; they will use dye cards along field 

edges to monitor for any offsite movement of pesticide. 

6. Before initiating operations, APHIS will obtain a concurrence from the U.S. Fish and Wildlife Service on 

protection measures that are required for endangered and threatened species, or their critical habitats. 

7. The program will report incidents of pesticide poisoning to the Texas Department of Health; information 

about the validity and probable cause will be used to develop additional protective measures, as 

necessary. 

Additional Notification Procedures 

1. For area residents who reside within 1⁄4-mile of treatments and who formally request (providing their name, 

address, and telephone number) special notification, program personnel will provide advance written or 

telephonic notification of the approximate times and dates of treatments. 

2. Growers participating in the program will be notified of treatment dates so that they may provide timely and 

appropriate notice of treatments and protective measures to persons in their employ or residing on their 

properties who could be exposed to pesticides. 

D. Additional Protective Measures for the Lower Rio Grande Valley 

The following protection measures have been adopted and made mandatory for the Lower Rio Grande Valley 

Boll Weevil Eradication Program. They may be more stringent than the operational procedures or mitigation 

measures that were published in the programmatic EIS, or the minimum site-specific protective measures that 

would be required to ensure that the proposed program will result in no significant environmental impact. 

Additional Precautions for Treatments 

1. During the first year of the program, all cotton fields will be treated after fields have reached “10 percent 

cracked boll” stage. Treatments will continue until fields are non-hostable following harvest. In 

subsequent years, no pesticide will be applied to a cotton field unless it has hostable fruit present and 

weevils are caught on it (trap triggers are exceeded), or a boll weevil infestation is detected by in-field 

inspection. 
A-7 

2. To the extent possible, malathion will be delivered and briefly stored in 260-gallon returnable, refillable totes 

(mini-bulk containers). The insecticide will be pumped directly from these containers into the spray 

equipment. This will minimize the potential for leakage or spillage and will prevent prolonged exposure 

to heat. 

Additional Notification Procedures 

1. Program personnel will establish a central telephone hot line for the public. The hot line will provide people 

with approximate times and places of treatment, program information and emergency referrals. The hot 

line will be available during the time the program is operational and will be able to provide information 

in English and Spanish. 

2. Program personnel will maintain in each office copies of the programmatic EIS and the EA, with the EA 

being available in both English and Spanish. 

Additional Monitoring and Reporting Procedures 

1. The environmental monitoring plan for this program will include (1) the use of dye cards to monitor possible 

pesticide drift to sensitive areas, (2) water sampling of major bodies of water that receive drainage from 

cotton fields, (3) sampling of selected streams and bodies of water for contamination from runoff, and 

(4) residue sampling on vegetation within sensitive areas. 

2. Program personnel will make available to the public, upon written request, data from program environmental 

monitoring efforts. 

3. The program will maintain a list of all complaints received regarding program pesticide applications to cotton 

fields. Each list entry will include a short summary on findings and resolution. 

4. Program personnel will prepare an annual report that relates, at a minimum, the types of treatments used 

(chemical and nonchemical), the number of applications for each treatment block, and the quantity of 

pesticide used; successive annual reports will include a summary comparison of pesticide use for each 

year. 

5. At the end of each year, program personnel will provide a report that assesses program success or the lack 

thereof. The report will generally address the problems encountered and how they were resolved. 

Succeeding reports will include comparisons of weekly or monthly boll weevil detections for each 

program year. Copies of the report will be sent to anyone who submits a written request. 
Protection measures for endangered & threatened species - 2011 B-1 

Protection Measures for Endangered, Threatened, and Proposed Species as 

part of the 2011 Boll Weevil Control Program in Texas 

KEY

STATUS: E=Endangered; E,CH=Endangered w/ Critical Habitat; T=Threatened; T,CH=Threatened w/ Critical Habitat; PE=Proposed Endangered; 

PT=Proposed Threatened w/Proposed Critical Habitat; PE,PCH=Proposed Endangered w/Proposed Critical Habitat; XN=Experimental Population.

CHANGES: Changes made in the table since last year are shaded in gray. 

PROTECTION MEASURES: NE=APHIS determines that the Boll Weevil Program will have No Effect on populations of this listed species.

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

MAMMALS

Bat, Mexican longnosed 

Leptonycteris navalis E No aerial use within 100 feet, no ground use within 60 feet of desert 

land with agave cactus. 

Bear, Louisiana black Ursus americanus luteolus T NE – Excluded by habitat 

Jaguarundi, Gulf Coast Herpailurus (=Felis) 

yagouaroundi cacomitli

E Monitor drift at habitat edge if field is within 300 feet of habitat. 

Jaguar Panthera onca E NE – Excluded by rarity/habits 

Manatee, West Indian Trichechus manatus E, CH NE – Excluded by habitat 

Ocelot Leopardus (=Felis) pardalis E Monitor drift at habitat edge if field is within 300 feet of habitat. 

Wolf, gray, lower 48 

States 

Canis lupus E, CH, XN NE – Excluded by habitat 

BIRDS

Crane, whooping Grus americana E, CH, XN Trained observer at site prior to each treatment. If crane is present, 

postpone treatment. 

Curlew, Eskimo Numenius borealis E NE – Excluded by rarity 

Eagle, bald 

(Protection measures 

remain in place for 

B&GE P Act) 

Haliaeetus leucocephalus Delisted No aerial or ground applications within 1,500 feet of nest when adults, 

nestlings, or fledglings are present at a nest site. Eagle presence will be 

established by a trained observer after repeated observations at the nest 

site before any treatment. No use within 60 feet of large water bodies 

(25 feet across) within a 1 mile radius of the nest site. 

Falcon, northern 

aplomado 

Falco femoralis 

septentrionalis

E No aerial use within 1 mile or ground use within 1⁄4 mile of nesting sites 

or release stations. 

Flycatcher, 

southwestern willow 

Empidonax traillii extimus E, CH No aerial use within 100 feet or ground use within 60 feet of habitat 

edge. Monitor for drift. 

Owl, Mexican spotted Strix occidentalis lucida T, CH NE – Excluded by habitat 

Pelican, brown Pelecanus occidentalis delisted NE – Excluded by habitat 

Plover, piping Charadrius melodus T, CH NE – Migratory and excluded by habitat 

Prairie-chicken, 

Attwater’s greater 

Tympanuchus cupido attwateri E Avoid drift into potential habitat. Monitor drift if cotton fields within 

300 feet of potential habitat. 

Tern, least (Interior) Sterna antillarum E No aerial or ground use within 300 feet of a colony and no use within 

60 feet of the water’s edge for 2.5 mile radius around the colony. 

Monitor for run-off. 
Protection measures for endangered & threatened species - 2011 B-2 

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

Vireo, black-capped Vireo atricapillus E From March 1 to Sept 1 implement the following measures: 

TX - Avoid drift into potential habitat. Monitor drift if cotton fields 

within 500 feet of potential habitat. No fly-over habitat. Swaths parallel 

to habitat edge. OK - Aerial application is prohibited within 100 feet 

of habitat, and ground applications are prohibited within 60 feet of 

habitat. 

Warbler, goldencheeked 

Dendroica chrysoparia E From March 1 to August 1 implement the following measures: 

Avoid drift into potential habitat. Monitor drift if cotton fields within 

500 feet of potential habitat. No fly-over habitat. Swaths parallel to 

habitat edge. 

Woodpecker, redcockaded Picoides (=Dendrocopos) 

borealis

E No aerial use within 100 feet or ground use within 60 feet of habitat 

edge. Monitor for drift 

REPTILES

Sea turtle, green Chelonia mydas E, T, CH NE – Excluded by habitat 

Sea turtle, hawksbill Eretmochelys imbricata E, CH NE – Excluded by habitat 

Sea turtle, Kemp's 

ridley 

Lepidochelys kempii E NE – Excluded by habitat 

Sea turtle, leatherback Dermochelys coriacea E, CH NE – Excluded by habitat 

Sea turtle, loggerhead Caretta caretta T NE – Excluded by habitat 

Snake, Concho water Nerodia paucimaculata (= 

harteri)

T, CH No aerial use within 100 feet or ground use within 60 feet of habitat 

edge. Monitor drift, water, and run-off. 

AMPHIBIANS

Salamander, Barton 

Springs 

Eurycea sosorum E No use within 60 feet of any drainage points that enter into recharge 

areas of the Edwards Aquifer. Monitor for run-off. 

Salamander, San 

Marcos 

Eurycea nana T, CH No use within 60 feet of any drainage points that enter into recharge 

areas of the Edwards Aquifer. Monitor for run-off. 

Salamander, Texas 

blind 

Typhlomolge rathbuni E No use within 60 feet of any drainage points that enter into recharge 

areas of the Edwards Aquifer. Monitor for run-off. 

Toad, Houston Bufo hustonensis E, CH No aerial use within 100 feet or ground use within 60 feet of habitat 

edge. Monitor drift, water if field within 500' of habitat, and run-off. 

FISH

Darter, fountain Etheostoma fonticola E, CH No use within 60 feet of identified aquatic habitat or recharge areas of 

the Edwards Aquifer. Monitor for run-off. 

Gambusia, Big Bend Gambusia gaigeii E NE – Excluded by habitat (only wild population in protected pond in 

National Park) 

Gambusia, Clear Creek Gambusia heterochir E No aerial use within 100 feet, no ground use within 60 feet of identified 

aquatic habitat. Monitor for drift and run-off. 

Gambusia, Pecos Gambusia nobilis E No aerial use within 100 feet, no ground use within 60 feet of identified 

aquatic habitat. Monitor for drift and run-off. 

Gambusia, San Marcos Gambusia georgei E, CH No use within 60 feet of identified aquatic habitat or recharge areas of 

the Edwards Aquifer. Monitor for run-off. 

Minnow, Devil’s River Dionda diaboli E, CH No aerial use within 100 feet and no ground use within 60 feet of 

identified aquatic habitat. Monitor for drift and run-off. 

Minnow, Rio Grande 

Silvery 

Hybognathus amarus E, CH No use within 60 feet of identified aquatic habitat. Monitor for run-off.
Protection measures for endangered & threatened species - 2011 B-3 

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

Pupfish, Comanche 

Springs 

Cyprinodon elegans E No aerial use within 100 feet, no ground use within 60 feet of identified 

aquatic habitat. Monitor for drift and run-off. 

Pupfish, Leon Springs Cyprinodon bovinus E, CH No aerial use within 100 feet, no ground use within 60 feet of identified 

aquatic habitat and recharge areas of springs. Monitor for run-off. 

Shiner, Arkansas River Notropis girardi T, CH No use within 60 feet of identified aquatic habitat. Monitor for run-off.

SNAILS

Snail, Pecos assiminea Assiminea pecos E, CH No use within 60 feet of identified aquatic habitat. Monitor for run-off.

INSECTS

Beetle, American 

burying 

Nicrophorus americanus E Avoid drift into potential habitat of beetle (=non-cultivated land) at the 

edge of fields in counties with species. Aerial swaths parallel to edge 

of beetle habitat. When possible, spray field edges with beetle habitat 

only from mid morning to late afternoon during March to November. 

Beetle, Coffin Cave 

mold 

Batrisodes texanus E No use within 60 feet of any drainage points from which run-off might 

enter cave or crevice entrance. Monitor for run-off. 

Beetle, Comal Springs 

dryopid 

Stygoparnus comalensis E, CH No use within 60 feet of any drainage points that enter into recharge 

areas of the Edwards Aquifer. Monitor for run-off. 

Beetle, Comal Springs 

riffle 

Heterelmis comalensis E, CH No use within 60 feet of any drainage points that enter into recharge 

areas of the Edwards Aquifer. Monitor for run-off. 

Beetle, Helotes mold Batrisodes venyivi E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

Beetle, Kretschmarr 

Cave mold 

Texamaurops reddelli E No use within 60 feet of any drainage points from which run-off might 

enter cave or crevice entrance. Monitor for run-off. 

Beetle, Tooth Cave 

ground 

Rhadine persephone E No use within 60 feet of any drainage points from which run-off might 

enter crevice or crevice entrance. Monitor for run-off. 

Rhadine exilis Rhadine exilis E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

Rhadine infernalis Rhadine infernalis E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

ARACHNIDS

Meshweaver, Bracken 

Bat Cave 

Cicurina venii E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

Harvestman, Bee 

Creek Cave 

Texella reddelli E No use within 60 feet of any drainage points from which run-off might 

enter cave or crevice. Monitor for run-off. 

Harvestman, Bone 

Cave 

Texella reyesi E No use within 60 feet of any drainage points from which run-off might 

enter cave or crevice. Monitor for run-off. 

Harvestman, 

Cokendolpher Cave 

Texella cokendolpheri E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

Pseudoscorpion, Tooth 

Cave 

Tartarocreagris 

(=Microcreagris) texana

E No use within 60 feet of any drainage points from which run-off might 

enter cave or crevice. Monitor for run-off. 

Spider, Government 

Canyon Bat Cave 

Neoleptoneta microps E To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

Meshweaver, Madla’s 

Cave 

Cicurina madla E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

Meshweaver, Robber 

Baron Cave 

Cicurina baronia E, CH To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 
Protection measures for endangered & threatened species - 2011 B-4 

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

Spider, Tooth Cave Neoleptoneta (=Leptoneta) 

myopica

E No use within 60 feet of any drainage points from which run-off might 

enter cave or crevice. Monitor for run-off. 

Meshweaver, 

Government Canyon 

Bat Cave 

Cicurina vespera E To protect invertebrate prey base (e.g., crickets), no ground use within 

320 feet and no aerial use within 1320 feet of cave or crevice entrance. 

CRUSTACEANS

Amphipod, Peck’s 

Cave 

Stygogromus (=Stygonectes) 

pecki 

E, CH No use within 60 feet of any drainage points that enter into recharge 

areas of the Edwards Aquifer. Monitor for run-off. 

PLANTS

Ashy dogweed Thymophylla (=Dyssodia) 

tephroleuca

E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators 

with no flying over pollinator habitat. When possible, spray during 

plant’s flowering period (February to November) only in the early 

dawn (no later than 1 hour after sunrise) or in early evening (6 pm or 

later) for a distance of up to 1⁄4 mile from plant habitat. 

Black lace cactus Echinocereus reichenbachii 

var. albertii (E. 

melanocentrus)

E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (late March to June) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Bunched cory cactus Coryphantha ramillosa T NE – Excluded by habitat 

Chisos Mountains 

hedgehog cactus 

Echinocereus chisoensis 

chisoensis

T Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (March to July) only in the early dawn (no later than 

1 hour after sunrise) or in early evening (6 pm or later) for a distance of 

up to 1⁄4 mile from plant habitat. 

Davis’ green pitaya Echinocereus viridiflorus var. 

davisii (E. davisii)

E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (March) only in the early dawn (no later than 1 hour 

after sunrise) or in early evening (6 pm or later) for a distance of up to 

1⁄4 mile from plant habitat. 

Geocarpon minimum

(=Sci. Name) 

Geocarpon minimum T NE – Excluded by habitat 

Hinckley oak Quercus hinckleyi T NE – No insect pollination 

Johnston’s frankenia Frankenia johnstonii E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (November to April) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 
Protection measures for endangered & threatened species - 2011 B-5 

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

Large-fruited sandverbena 

Abronia macrocarpa E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (late March to early June) only in the early dawn (no 

later than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1 mile from plant habitat. 

Little Aguja pondweed Potamogeton clystocarpus E No use within 60 feet of identified aquatic habitat. Monitor for run-off. 

Lloyd’s Mariposa 

cactus 

Echinomastus (=Echinocactus, 

=Sclerocactus, =Neolloydia) 

mariposensis

T Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (consult biologist) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Navasota ladies’-

tresses 

Spiranthes parksii E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (October to November) only in the early dawn (no 

later than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1 mile from plant habitat. 

Nellie cory cactus Coryphantha (=Escobaria, 

=Mammillaria) minima (=C. 

nellieae)

E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (consult biologist) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Pecos (= puzzle) 

sunflower 

Helianthus paradoxus T, CH Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (September to November) only in the early dawn (no 

later than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Slender rush-pea Hoffmannseggia tenella E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (February to June) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Sneed pincushion 

cactus 

Coryphantha sneedii 

(=Escobaria, =Mammillaria) 

var. sneedii

E NE – Excluded by habitat 

South Texas ambrosia Ambrosia cheiranthifolia E NE – No insect pollination 
Protection measures for endangered & threatened species - 2011 B-6 

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

Star cactus Astrophytum asteris E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (March to June) only in the early dawn (no later than 

1 hour after sunrise) or in early evening (6 pm or later) for a distance 

of up to 1⁄4 mile from plant habitat. 

Terlingua Creek cat’seye 

Cryptantha crassipes E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (March to early June) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Texas ayenia Ayenia limitaris E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (November to April) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Texas poppy-mallow Callirhoe scabriuscula E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat.. When possible, spray during plant’s 

flowering period (late April to mid-June) only in the early dawn (no 

ater than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Texas prairie dawnflower (=Texas 

bitterroot) 

Hymenoxys texana E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (late March to early April) only in the early dawn (no 

later than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1 mile from plant habitat. 

Texas snowbells Styrax texanus E NE – Excluded by habitat 

Texas trailing phlox Phlox nivalis ssp. texensis E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat.. When possible, spray during plant’s 

flowering period (March to April) only in the early dawn (no later than 

1 hour after sunrise) or in early evening (6 pm or later) for a distance 

of up to 1⁄4 mile from plant habitat. 

Texas wild-rice Zizania texana E, CH NE – No insect pollination 
Protection measures for endangered & threatened species - 2011 B-7 

COMMON NAME SCIENTIFIC NAME STATUS PROTECTION MEASURES 

Tobush fishhook 

cactus 

Ancistrocactus tobuschii E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (mid-February to April) only in the early dawn (no 

later than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1⁄4 mile from plant habitat. 

Todsen’s pennyroyal Hedeoma todsenii E, CH NE – Excluded by habitat 

Walker’s manioc Manihot walkeri E Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (April to September) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1 mile from plant habitat. 

White bladderpod Lesquerella pallida E NE – Excluded by habitat 

Zapata bladderpod Lesquerella thamnophila E, CH Avoid drift into potential habitat of pollinators (=areas with native, 

unmown vegetation) and monitor drift if cotton field is within 500 feet 

of pollinator habitat. Swaths parallel to habitat edge of pollinators with 

no flying over pollinator habitat. When possible, spray during plant’s 

flowering period (early April to May) only in the early dawn (no later 

than 1 hour after sunrise) or in early evening (6 pm or later) for a 

distance of up to 1 mile from plant habitat. 

Zuni (=Rhizome) 

fleabane 

Erigeron rhizomatus T NE – Excluded by habitat 
Endangered and Threatened Species Site Reporting Form - 2011

Use additional copies as needed. Prior to the start of applications of malathion, return the completed form to: Dr. Robert Baca, USDA-APHIS-PPQ, 4700 River Road, Unit 150, Room 5A-04.b, Riverdale, MD 20737 Work unit/District/Zone/Program:_____________________________________________Sta

Species Field Number(s) Acres GPS Coordinates Distance to Field Comments 
 C-1 

ENVIRONMENTAL MONITORING SUPPLIES CHECKLIST

SUPPLIES TO BRING EACH TIME YOU GO TO A SAMPLING SITE

Monitoring plan/SOP’s Obtain from ECT Thermometer 

Field log notebook Ice chest/wet or blue ice Obtain locally 

Compass Baby wipes 

Wind gauge 2060 monitoring forms 

Indelible marker Packing/strapping tape 

A.R.S.E. (Run-off Sampling) Dye Cards

Plexiglas cover Oil sensitive dye cards 

8"x 8" mesh screen Water sensitive dye cards 

Tent pegs/nails 5' bamboo poles/stakes 

Funnels attached to caps Paper/alligator clips 

500 ml bottles Tacks 

4" PVC pipe, 14" long 4" x 4" plastic bags 

Post hole digger 12" x 12" plastic bags 

Pea gravel Tweezers/forceps 

Large rocks/bricks disposable gloves 

Bamboo pole/flagging tape Water Samples

collapsible cubitainer Dissolved oxygen kit 

Sodium sulfate (small vials) collapsible cubitainer 

pH paper/pH meter Sodium sulfate (small vials) 

Sulfuric acid (squeeze bottle) pH paper/pH meter 

Styrofoam ‘coffin’ Acid or base (squeeze bottle) Obtain locally

Vegetation/Fish/Insect Samples Sediment Samples

Pruning sheers/scissors Dredge tied to strong rope

Aluminum foil envelopes 3 gallon galvanized pail

Strapping tape Hand trowel

3" mesh screen

 Aluminum foil envelopes
 C-2 

Soil Samples Swab/Wipe Samples

Soil core sampler 3” x 3” sterile cotton pads 

with resealable plastic bag 

3 gallon galvanized pail Metric ruler 

Hand trowel Pencil 

3" mesh screen Disposable gloves 

Aluminum foil envelopes Isopropyl alcohol Obtain locally

Baby wipes 

Neat (Pure) Chemical Formulations Miscellaneous Supplies

Amber glass bottle Labels 

Parafilm Styrofoam coolers/mailers 

Small mailing tubes Freezer Obtain locally

Cat litter/packing material 2 oz bottle for honey samples 

Disposable pipette Resealable plastic bags: 

Pipetting bulb 4" x 4" 

Disposable gloves 6" x 6" 

Protective eyewear 8" x 8" 

 12" x 12" 

Program: _________________________________ Requested by: ______________________________ 

Date: _____________________________________ Phone: ____________________________________ 

Address: ____________________________________________________________________________________ 

____________________________________________________________________________________________ 

____________________________________________________________________________________________ 

To order supplies, indicate the quantity of each items needed. Fax a copy of this form to the USDA-APHISCPHST Gulfport Lab at 228-822-3209 or 228-822-3137. If fax machines are not working, leave a message 

with the CPHST Gulfport Lab supplies manager at 228-822-3106. Please realize that it may be difficult to 

completely fill order for large quantities of materials. 

Note: This is not an exhaustive supply list...items that are not listed here may be available through the 

CPHST Gulfport Lab. Not all supplies listed above are required for all pest control programs.